[DETAILED DESCRIPTION OF THE INVENTION]
[Technical Field to Which the Invention Belongs]
[0001] The present invention relates to a packing material for solid phase extraction, which
has a specific exclusion limit molecular weight or a specific pore size; a column
and a cartridge for solid phase extraction, each using the packaging material; and
a process for treating a medical sample, which uses the column or cartridge.
[Background Art]
[0002] In many cases, a liquid-liquid extraction method has been heretofore used for extracting
a sample from a liquid, however, this method has a problem in that the operation is
cumbersome, a solvent is used in a large amount and the solvent used greatly affects
the environment and human body. In recent years, with the progress of synthesis methods,
a solid phase extraction method using silica-type or synthetic polymer-type porous
particles and capable of treating a large amount of sample through a simple operation
using a small amount of solvent by virtue of automation is used.
[0003] The packing material for use in the solid phase extraction uses an inorganic substrate
such as silica gel or chemical bonding-type silica gel obtained by chemically modifying
the surface of silica gel, or an organic substrate such as a synthetic polymer-type
substrate represented by polystyrene-divinylbenzene or a substrate obtained by chemically
modifying the surface thereof.
[0004] Heretofore, inorganic or organic packing materials are known as the packing material
for use in the solid phase extraction. For example, JP-A-6-258203 (the term "JP-A"
as used herein means an "unexamined published Japanese patent application") describes
a cartridge column for solid phase extraction, which is packed with a copolymer of
divinylbenzene and polyhydric alcohol poly(meth)acrylic acid ester, however, in this
patent publication, discussed are only the hydrophobicity and hydrophilicity on the
surface of the crosslinked copolymer particle.
[0005] As such, the packing material for solid phase extraction has been studied only on
the chemical properties thereof, such as hydrophobicity or hydrophilicity on the particle
surface, but studies on the physical properties such as pore size distribution have
not been satisfactorily made.
[Problems to be Solved by the Invention]
[0006] The object of the present invention is to obtain a packing material having excellent
properties by studying on the physical properties such as pore size range of the packing
material while taking account of the chemical properties such as hydrophobicity or
hydrophilicity on the particle surface of conventional packing materials for solid
phase extraction.
[Means to Solve the Problems]
[0007] As a result of extensive investigations to overcome the above-described problems,
the present inventors have found that a packing material for solid phase extraction,
ensuring excellent recovery of sample can be obtained by controlling the pore size
distribution. The present invention has been accomplished based on this finding.
[0008] More specifically, the present invention relates to the following matters.
[1] A packing material for solid phase extraction, comprising particles having an
exclusion limit molecular weight of from 1×103 to 1.5×104 in gel permeation chromatography using a standard polystyrene as the measuring sample.
[2] The packing material for solid phase extraction as described in [1] above, wherein
the particle is a synthetic polymer particle obtained by polymerizing monomers containing
at least a crosslinkable monomer.
[3] The packing material for solid phase extraction as described in [2] above, wherein
the synthetic polymer particle is a polymer of at least a crosslinkable monomer (A)
and a non-crosslinkable monomer (B).
[4] The packing material for solid phase extraction as described in [3] above, which
contains an aromatic divinyl compound as the crosslinkable monomer (A) in an amount
of 30% by mass or more based on the total amount of monomers.
[5] The packing material for solid phase extraction as described in [3] or [4] above,
which contains a polyhydric alcohol poly(meth)acrylic acid ester as the crosslinkable
monomer (A) in an amount of 10% by mass or more based on the total amount of monomers.
[6] The packing material for solid phase extraction as described in any one of [3]
to [5] above, which contains an N-vinylcarboxylic acid amide as the non-crosslinkable
monomer (B) in an amount of 5 to 60% by mass based on the total amount of monomers.
[7] The packing material for solid phase extraction as described in [6] above, wherein
the N-vinylcarboxylic acid amide is N-vinylacetamide.
[8] The packing material for solid phase extraction as described in any one of [1]
to [7] above, which is packed into a column, a cartridge or a reservoir on use.
[9] The packing material for solid phase extraction as described in any one of [1]
to [8] above, which is used for concentrating an objective component and/or removing
impurities or contaminants.
[10] The packing material for solid phase extraction as described in any one of [1]
to [9] above, which has an average particle size of 1 to 200 µm.
[11] A column for solid phase extraction] above, which is packed with the packing
material for solid phase extraction described in any one of [1] to [10] above.
[12] A cartridge for solid phase extraction] above, which is packed with the packing
material for solid phase extraction described in any one of [1] to [10].
[13] The column for solid phase extraction as described in [11] above, which is used
for concentrating an objective component and/or removing impurities or contaminants.
[14] The cartridge for solid phase extraction as described in [12] above, which is
used for concentrating an objective component and/or removing impurities or contaminants.
[15] A process for treating an environment- or medical sample, which uses the column
for solid phase extraction described in [11] or [13] above.
[16] A process for treating an environment- or medical sample, which uses the cartridge
for solid phase extraction described in [12] or [14] above.
[17] The process for treating an environment- or medical sample as described in [15]
or [16] above, which is used for the treatment of a protein component-containing sample.
[0009] The exclusion limit molecular weight of the particles is 1,000 to 15,000, preferably
7,000 to 15,000. The particle size is preferably 1 to 200 µm, more preferably 1 to
100 µm, and even more preferably 20 to 70 µm. The surface area of the particles is
preferably 350 to 800 m
2/g, more preferably 450 to 700 m
2/g and still more preferably 550 to 670 m
2/g. Therefore, particularly preferred particles have an exclusion molecular weigth
of 7,000 to 15,000, a particle size of 1 to 100 µm, and a surface area of 550 to 670
m
2/g.
[Mode for Carrying Out the Invention]
[0010] The packing material for solid phase extraction of the present invention is a particle
having an exclusion limit molecular weight of from 1×10
3 to 1.5×10
4 in gel permeation chromatography using a standard polystyrene as the measuring sample.
This particle may use an inorganic substrate or an organic substrate, however, a synthetic
polymer-type packing material for solid phase extraction using an organic substrate
is preferred on taking account of easiness of the bulk synthesis, good reproduction
in the control of pore size and the like. Examples of the synthetic polymer using
an organic substrate include polystyrene-divinylbenzene type; poly(meth)acrylate type
such as polyacrylate, glycidyl methacrylate and ethylene glycol dimethacrylate, and
various copolymers thereof.
[0011] In the present invention, the packing material for solid phase extraction is preferably
obtained by polymerizing monomers containing at least a crosslinkable monomer (A)
or by copolymerizing a crosslinkable monomer (A) and a non-crosslinkable monomer (B).
The packing material for solid phase extraction of the present invention includes
polymers obtained by polymerizing only the crosslinkable monomer (A) as the monomer
without containing the non-crosslinkable monomer (B).
[0012] The crosslinkable monomer (A) for use in the present invention is not particularly
limited as long as it polymerizes with a monomer used and examples thereof include
aromatic compounds having two or more vinyl groups, such as divinylbenzene, divinyltoluene,
divinylxylene and divinylnaphthalene; and polyhydric alcohol poly-(meth)acrylic acid
esters such as ethylene glycol di(meth)acrylate, polyethylene glycol di(meth)acrylate,
propylene glycol di(meth)acrylate, polypropylene glycol di(meth)acrylate, glycerin
di(meth)acrylate, trimethylolpropane tri(meth)acrylate, tetramethylolmethane tri-(meth)acrylate
and tetramethylolmethane tetra(meth)acrylate.
[0013] The aromatic compound having two or more vinyl groups, such as divinylbenzene, divinyltoluene,
divinylxylene and divinylnaphthalene, is preferably contained in an amount of 30%
by mass or more, more preferably 45% by mass or more, based on the total amount of
monomers. Among these aromatic compounds having two or more vinyl groups, divinylbenzene
is preferably used in view of easy availability.
[0014] The purity of the aromatic compound having two or more vinyl groups, such as divinylbenzene,
used in the present invention is not particularly limited, however, an aromatic compound
having a purity of 55% by mass or more is preferably used.
[0015] In the present invention, a polyhydric alcohol poly(meth)acrylic acid ester can also
be used as the crosslinkable monomer (A). Among polyhydric alcohol poly(meth)acrylic
acid esters, ethylene glycol di(meth)acrylate and glycerin di(meth)acrylate are preferred
on taking account of the reactivity, operability at the reaction and the balance of
swelling degree in the copolymer particles produced. The polyhydric alcohol poly(meth)acrylic
acid ester is preferably contained in an amount of 10% by mass or more, more preferably
from 20 to 25% by mass, based on the total amount of monomers.
[0016] Examples of the non-crosslinkable monomer (B) for use in the present invention include
N-vinylcarboxylic acid amides such as N-vinylformamide, N-vinylacetamide, N-vinylpropionamide,
N-(propenyl-2-yl)formamide and N-(propenyl-2-yl)acetamide. Among these, in view of
the hydrophilicity and the operability at the reaction, N-vinylacetamide is preferably
used. The N-vinylacetamide is contained in an amount of 5 to 60% by mass, preferably
from 5 to 30% by mass, based on the total amount of monomers.
[0017] The packing material for solid phase extraction of the present invention is porous
and for the purpose of imparting the porosity, a diluent is added to a mixture of
monomers at the polymerization. The diluent which can be used is an organic solvent
having properties such that it dissolves in the monomer mixture, is inactive to the
polymerization reaction and does not dissolve the polymer produced. Examples thereof
include aromatic hydrocarbons such as toluene, xylene, ethylbenzene and diethylbenzene;
saturated hydrocarbons such as hexane, heptane, octane and decane; alcohols such as
isoamyl alcohol, hexyl alcohol, octyl alcohol and 2-ethylhexyl alcohol; aliphatic
halogenated hydrocarbons such as dichloromethane, dichloroethane and trichloroethane;
and aliphatic or aromatic esters such as ethyl acetate, butyl acetate, dimethyl phthalate
and diethyl phthalate. These organic solvents used as a diluent can be used individually
or in combination of two or more thereof.
[0018] In the case of a copolymer having a pore size such that the exclusive limit molecular
weight in gel permeation chromatography using as a standard polystyrene as the sample
is from 1×10
3 to 1.5×10
4, toluene or a mixture of toluene and an alcohol such as 2-ethylhexyl alcohol is preferably
used.
[0019] The amount of the diluent added is preferably from 10 to 300% by mass based on the
total amount of the crosslinkable monomer (A) and the non-crosslinkable monomer (B)
and in the case of a copolymer having a pore size such that the exclusive limit molecular
weight for polystyrene in gel permeation chromatography is from 1×10
3 to 1.5×10
4, the amount of the diluent added is preferably from 50 to 150% by mass.
[0020] The copolymer particle of the present invention is produced by suspension polymerization
in an aqueous medium containing an appropriate dispersion stabilizer. In this case,
the polymerization initiator used is not particularly limited as long as it is a known
radical polymerization initiator capable of generating a radical, and examples thereof
include azo-type initiators such as 2,2'-azobisisobutyronitrile and 2,2'-azobis(2,4-dimethylvaleronitrile).
The concentration of the polymerization initiator is preferably from 0.1 to 5% by
mass based on the monomers.
[0021] In the present invention, the polymerization reaction can be performed by the suspension
polymerization method where a monomer solvent containing a diluent is stirred in an
aqueous medium containing an appropriate dispersion stabilizer and suspended and then
the polymerization is allowed to proceed. The dispersion stabilizer may be a known
dispersion stabilizer and in general, a water-soluble polymer compound such as gelatin,
sodium polyacrylate, poly(vinyl alcohol), hydroxyethyl cellulose or carboxymethyl
cellulose is used. The concentration of the dispersion stabilizer used is preferably
from 0.1 to 5% by mass based on the aqueous medium. The aqueous medium is a medium
mainly comprising water and in the medium, a salt and other water-soluble components
may be dissolved in addition to water.
[0022] The polymerization reaction is preferably performed by dissolving a salt in the aqueous
medium for the purpose of suppressing the monomers from dissolving in the aqueous
medium. Examples of the salts used include sodium chloride, calcium chloride and sodium
sulfate.
[0023] The N-vinylcarboxylic acid amide has a high solubility in water, therefore, a salt
is preferably used in a high concentration so as to suppress the dissolution. The
salt used and the concentration thereof are not particularly limited but since the
solubility varies depending on the salt used, for example, sodium chloride is preferably
used in an amount of 0.1 to 15% by mass and calcium chloride is preferably used in
an amount of 1 to 40% by mass, based on the aqueous medium.
[0024] If the mass ratio (liquid ratio) of the aqueous dispersion medium phase containing
a dispersion stabilizer and a salt to the organic solvent phase formed by mixing a
monomer mixture containing the crosslinkable monomer (A) and the non-crosslinkable
monomer (B) with a diluent and dissolving a polymerization initiator therein is excessively
large, the N-vinylcarboxylic acid amide is distributed into the aqueous dispersion
medium phase because of its high solubility in water and the yield decreases. On the
other hand, if the liquid ratio is too small, the suspension dispersion of the organic
solvent phase becomes unstable. Accordingly, the ratio of the aqueous dispersion phase
to the organic solvent phase is preferably from 2:1 to 10:1.
[0025] The polymerization reaction is performed, after purging with nitrogen gas, by heating
the reaction system to 40 to 100°C with ordinary stirring for 5 to 16 hours under
an atmospheric pressure. The organic solvent phase becomes spherical particles by
the stirring and the particles disperse in the aqueous medium, whereby the reaction
proceeds. At this time, the polymerization proceeds in the state such that individual
particles contain a diluent, and the polymer grows as a network polymer, as a result,
when the diluent is removed later, porous particles can be obtained.
[0026] After the reaction, the particles can be easily separated by filtration or the like
and the diluent can be easily removed through washing with a solvent such as acetone
or methanol and then drying. The thus-obtained packing material having a pore size
controlled to a specific range is classified into a particle size of 1 to 200 µm,
preferably from 1 to 100 µm, more preferably from 20 to 70 µm, and then used as a
packing material for solid phase extraction.
[0027] The packing material for solid phase extraction of the present invention can be widely
applied to the concentration or removal of trace components and in particular, can
be used by packing it into a reservoir of a column or a cartridge.
[0028] In the solid phase extraction method, the packing material manufactured for use in
the solid phase extraction is used by packing it into a container called a reservoir
of a column or a cartridge, however, the shape and the constructive material of the
container such as column, cartridge and reservoir are not particularly limited as
long as the container is insoluble in the organic solvent used and impurities do not
dissolve out from the container itself during the operation of solid phase extraction.
[0029] In the present invention, the cartridge means a cylindrical container having an internal
diameter of 2 to 6 mmφ and a length of 10 to 30 mm, where both ends are stopped by
frit or filter to prevent flowing out of gel and the frit or filter is fastened by
a cap having a hole of 0.1 to 1 mm in the center. The cartridge by itself has no connector
necessary for flowing a liquid and therefore, is used by fixing it to an exclusive
cartridge holder, guard holder or reservoir container called holder.
[0030] The column is a cylindrical container having an internal diameter of 2 to 6 mmφ and
a length of from 10 to 50 mm with the both ends being stopped by an end-fitting. The
end-fitting has a connector together with frit or filter for preventing the flowing
out of gel, therefore, the column means a container which can be directly connected
to allow the flowing of a liquid.
[0031] Examples of the constructive material for the cartridge or column include inorganic
materials such as stainless steel and glass, and synthetic resin materials such as
polyethylene, polypropylene and polyether ether ketone. Among these, on considering
the simplicity, convenience and cost, a polyethylene-made container is preferred and
examples thereof include an injector-type container having a volume of 1 to 200 mL,
preferably from 1 to 100 mL.
[0032] In the column or cartridge for solid phase extraction, a porous plate called filter
or frit having a pore of 5 to 200 µm, preferably from 10 to 50 µm, is set to the both
ends of the column or reservoir so as to prevent the passing through of the packing
material during the operation of solid phase extraction. The constructive material
of the filter or frit is not particularly limited but examples thereof include stainless
steel, glass, polyethylene and polytetrafluoroethylene. Among these, polyethylene
is preferred in view of the cost and operability.
[0033] The amount of the packing material for solid phase extraction packed in the reservoir
of column or cartridge varies depending on the bulk density of particles or the concentration
ratio of the sample, however, the amount packed is usually from 30 to 500 mg, preferably
from 50 to 300 mg, based on the volume of 3 mL in each case.
[0034] Use of the column or cartridge packed with the packing material for solid phase extraction
of the present invention is not particularly limited, however, in view of the properties
of the packing material for solid phase extraction, the column or cartridge can be
used for concentrating a trace objective substance contained in an extra dilute solution
and/or for easily removing impurities or contaminants present together, at the analysis
treatment of an environment-related sample, a medical sample or the like. Furthermore,
the column or cartridge can be suitably used for the measurement of harmful substances
such as agricultural chemicals in river water, the measurement of residual agricultural
chemicals in farm products and the measurement of drugs in serum. The column or cartridge
is effective, for example, in the adsorption and removal of albumin and the like,
however, the use is not limited thereto.
[0035] The process for treating an environment-related sample or a medical sample of the
present invention is a solid phase extraction process where an objective component
is extracted in the solid phase using the above-described packing material and/or
column or cartridge for solid phase extraction. The treating process of the present
invention is to concentrate a trace objective substance contained in an extra dilute
solution and/or remove impurities or contaminants present together at the analysis
of various samples and can be applied as a pretreatment and/or a posttreatment in
various analyses.
[Examples]
[0036] The present invention is described in greater detail below by referring to the Examples,
however, the present invention is by no means limited to these Examples.
Example 1:
[0037] 18.75 g of pulverized N-vinylacetamide (NVA monomer, produced by Showa Denko K.K.)
was dissolved in a mixed solution of a monomer phase containing 41.25 g of divinylbenzene
having a purity of 81% (DVB-H, produced by Sankyo Kasei K.K.) and 15.00 g of ethylene
glycol dimethacrylate (NK Ester 1G, produced by Shin Nakamura Kagaku Kogyo K.K.) and
a diluent phase containing 30.28 g of toluene (produced by Wako Junyaku Kogyo K.K.)
and 10.10 g of 2-ethylhexanol (produced by Wako Junyaku Kogyo K.K.) and subsequently,
2.00 g of 2,2'-azobis(2,4-dimethylvaleronitrile) was dissolved therein to prepare
an oil phase.
[0038] In 286 mL of deionized water, 103.5 g of calcium chloride and 10.35 g of sodium chloride
were dissolved to prepare a salt solution. Subsequently, 4 g of polyvinyl alcohol
(Kuraray Poval PVA-224, produced by Kuraray K.K.) and 4 g of sodium chloride were
dissolved in 100 mL of deionized water and therefrom, 86 mL was sampled and added
to the salt solution. Furthermore, 6.4 mg of sodium nitrite was dissolved in 10 mL
of deionized water and therefrom, 7 mL was sampled and added into the salt solution.
The thus-prepared salt solution was used as the aqueous phase.
[0039] The oil phase and the aqueous phase were mixed and stirred at a high speed of 1,800
rpm for 5 minutes in Excel Auto Homogenizer (produced by Nihon Seiki Seisakusho K.K.)
to adjust the oil droplets to from 20 to 100 µm. Thereafter, the suspension was poured
into 1 L-volume separable flask and reacted for 6 hours by elevating the temperature
to 70°C while stirring at 100 rpm in a water bath in a nitrogen gas atmosphere. After
cooling, the copolymer particles produced were separated by filtration through a filter
paper of No. 101, washed with 2 L of deionized water and with 2 L of acetone, then
air-dried by spreading the particles on a stainless steel-made vat, and further dried
under reduced pressure at 60°C for 16 hours. The copolymer particles obtained were
classified into from 40 to 70 µm using a pneumatic classifier (MINI. CLASSIFIER, manufactured
by NIPPON PNEUMATIC MFG) to prepare a packing material for solid phase extraction.
(Measurement of Exclusion Limit Molecular Weight by Gel Permeation Chromatography)
[0040] Using a packer and a pump, the copolymer particles classified into from 40 to 70
µm were packed into a stainless steel-made column for liquid chromatography of 4.6
mm (inside diameter) × 150 mm (length) by an equilibrium slurry method to obtain a
packed column. This column was connected to a high performance liquid chromatograph,
tetrahydrofuran as a mobile phase was flown at a flow rate of 0.33 ml/min, and then
standard polystyrene Standards (Shodex (registered trade mark of Showa Denko) STANDARD
S series, dealing by Showa Denko K.K.) having an average molecular weight of 2,400,000,
1,070,000, 460,000, 156,000, 66,000, 28,500, 11,600, 7,000, 5,050, 3,250, 2,450, 1,680,
1,320, 980 or 580 and benzene each was injected. An elution time was determined from
the chromatogram obtained and an exclusion limit molecular weight was measured by
plotting the logarithm of average molecular weight for the ordinate and the elution
time for the abscissa on a graph.
[0041] The exclusion limit molecular weight obtained was 7,000.
(Measurement of Surface Area)
[0042] The measurement of the surface area was performed using COULTER SA3100 manufactured
by COULTER, as a result, the surface area of the copolymer particles was 635 m
2/g.
(Measurement 1 of Recovery by Solid Phase Extraction)
[0043] 250 mg of copolymer particles classified into from 40 to 70 µm were packed in a 3
mL-volume reservoir to prepare a cartridge for solid phase extraction and the measurement
of recovery was performed according to the following procedure.
1. The cartridge for solid phase extraction was set to a suction manifold.
2. 5 mL of acetonitrile was passed at 5 ml/min.
3. 5 mL of deionized water was passed at 5 ml/min.
4. 100 mL of a sample adjusted to 0.25 ppm as a sample for concentration was passed
at 5 mL/min and the sample was adsorbed in the cartridge for solid phase extraction.
5. 5 mL of deionized water was passed at 5 ml/min.
6. 5 mL of acetonitrile was passed at 5 ml/min and the eluate was recovered.
7. From the recovered eluate, 20 µl was sampled and analyzed by a high performance
liquid chromatograph and the area value thereof was determined.
8. Using as the standard sample the same substance as used for the sample adsorbed,
20 µl of a sample was adjusted to 5 ppm and analyzed by a high performance liquid
chromatograph and the area value thereof was determined.
9. The recovery was obtained by the area value of the sample for concentration/the
area value of the standard sample.
[0044] If the copolymer has a low capability of concentration, the sample is not adsorbed
to the copolymer and the recovery decreases. The results of the measurement of recovery
are shown in Table 1. The recovery was 85% or more and from this, it was revealed
that the copolymer was a packing material for solid phase extraction having an excellent
capability of concentrating a sample.
Example 2:
[0045] A copolymer was synthesized in the same manner as in Example 1 except for changing
the diluent phase to 37.50 g of toluene and 12.50 g of 2-ethylhexanol. The measurements
of the exclusion limit molecular weight by gel permeation chromatography, the surface
area and the recovery by solid phase extraction were also performed in the same manner
as in Example 1. The exclusion limit molecular weight obtained was 15,000, the surface
area was 601 m
2/g and as seen in Table 1, it was revealed, similarly to Example 1, that the copolymer
was a packing material for solid phase extraction having an excellent capability of
concentrating a sample.
Comparative Example 1:
[0046] A copolymer was synthesized and evaluated in the same manner as in Example 1 except
for changing the diluent phase to 49.90 g of toluene and 16.60 g of 2-ethylhexanol.
The exclusion limit molecular weight obtained by gel permeation chromatography was
25,000 and the surface area was 643 m
2/g. As seen from the results of measurement of the recovery by solid phase extraction
shown in Table 1, the recovery was low and the copolymer was a packing material for
solid phase extraction having a low capability of concentrating a sample.
Comparative Example 2:
[0047] A copolymer was synthesized and evaluated in the same manner as in Example 1 except
for changing the diluent phase to 77.91 g of toluene and 13.75 g of 2-ethylhexanol.
The exclusion limit molecular weight obtained by gel permeation chromatography was
60,000 and the surface area was 788 m
2/g. As seen from the results in Measurement 1 of Recovery by Solid Phase Extraction
shown in Table 1, the recovery was low and the copolymer was a packing material for
solid phase extraction having a low capability of concentrating a sample.
[Table 1]
| |
Recovery (%) |
| |
Example 1 |
Example 2 |
Comparative
Example 1 |
Comparative
Example 2 |
| Phenol |
101.7 |
87.2 |
59.0 |
53.8 |
| o-Chlorophenol |
100.8 |
87.0 |
57.4 |
50.9 |
| m-Chlorophenol |
99.0 |
87.9 |
55.6 |
48.5 |
| p-Chlorophenol |
100.4 |
88.5 |
55.8 |
50.0 |
| (Conditions for High Performance Liquid Chromatography) |
| Column |
Shodex (registered trade mark of Showa Denko K.K.) C18-5A (4.6 mmφ×150 mm) |
| Mobile phase |
acetonitrile/water = 40/60 (V/V) |
| Flow rate |
1.0 mL/min |
| Detector |
ultraviolet absorption detector |
| Measuring wavelength |
UV 254 nm |
| Amount of sample injected |
20 µL |
Example 3:
[0048] The copolymer particles (exclusion limit molecular weight: 7,000) obtained in Example
1 were classified into from 40 to 70 µm, 50 mg thereof was packed in a 1 mL-volume
reservoir to prepare a cartridge for solid phase extraction, and the measurement of
recovery was performed according to the following procedure.
(Measurement 2 of Recovery by Solid Phase Extraction)
[0049]
1. The cartridge for solid phase extraction was set to a suction manifold.
2. 1 mL of methanol was passed at 1 ml/min.
3. 1 mL of 50 mM sodium phosphate buffer solution (pH 6.0) was passed at 1 ml/min.
4. Samples for concentration obtained by dissolving ketoprofen, pindolol and prednisolone
into 2 mL of 50 mM sodium phosphate buffer solution (pH 6.0) containing 20 mg of bovine
serum albumin to a concentration of 0.2 ppm, 0.5 ppm and 1.0 ppm, respectively, each
was passed at 1 ml/min and adsorbed in the cartridge for solid phase extraction.
5. 1 mL of 50 mM sodium phosphate buffer solution (pH 6.0) containing 5% of methanol
was passed at 1 mL/min to perform the cleaning.
6. 1 mL of methanol was passed at 1 mL/min and the eluate was recovered.
7. From the recovered eluate, 20 µl was sampled and analyzed by a high performance
liquid chromatograph 1 or 2 and the area value was determined.
8. Using as the standard sample the same substance as used for the sample adsorbed,
20 µl of a sample was adjusted to 0.2 ppm, 1.0 ppm and 2.0 ppm, respectively and analyzed
by the high performance liquid chromatograph 1 and the area value thereof was determined.
9. 20 µL of a standard sample of 50 mM sodium phosphate buffer solution (pH 6.0) containing
10 mg/mL of bovine serum albumin was analyzed by the high performance liquid chromatograph
2 and the area value thereof was determined.
10. From the area value of the sample for concentration/the area value of the standard
sample, the recovery of each drug and the adsorption ratio (removal ratio) of bovine
serum albumin were determined.
Comparative Example 3:
[0050] Using a commercially available solid phase cartridge in which 50 mg of octadecyl
silica (exclusion limit molecular weight: 100,000) having a particle size of 40 to
70 µm was packed into a 1 mL-volume reservoir, the same operation as in Example 3
was performed, and the recovery of each drug and the adsorption ratio (removal ratio)
of albumin were determined.
[0051] In Example 3, it was verified that three kinds of drugs were effectively concentrated
and recovered and at the same time, albumin as high molecular weight impurities or
contaminants was mostly prevented from adsorbing.
[0052] On the other hand, in Comparative Example 3, recovery of some acidic or basic drugs
was low and moreover, bovine serum albumin slightly adsorbed, revealing that a problem
was present from the standpoint of pretreating a sample.
[Table 2]
| |
Recovery and Adsorption Ratio (%) |
| |
Example 3 |
Comparative Example 3 |
| Ketoprofen |
89.4 |
62.0 |
| Pindolol |
90.2 |
51.5 |
| Prednisolone |
88.0 |
86.8 |
| Bovine serum albumin |
0.1 |
2.5 |
| (Conditions for Measurement by High Performance Chromatograph 1) |
| Column |
Shodex (registered trade mark of Showa Denko K.K.) Silica C18 M 4D |
| Mobile phase |
acetonitrile/water = 40/60 |
| Flow rate |
1.0 mL/min |
| Detector |
ultraviolet absorption detector |
| Measuring wavelength |
UV 254 nm |
| Amount of sample injected |
20 µL |
| (Conditions for Measurement by High Performance Chromatograph 2) |
| Column |
Shodex (registered trade mark of Showa Denko K.K.) Protein KW-803 |
| Mobile phase |
100 mM sodium phosphate buffer solution (pH 6.5) |
| Flow rate |
1.0 mL/min |
| Detector |
ultraviolet absorption detector |
| Measuring wavelength |
UV 280 nm |
| Amount of sample injected |
20 µL |
[Effects of the Invention]
[0053] The packing material for solid phase extraction of the present invention is a packing
material ensuring excellent recovery obtained by adjusting the pore size of the packing
material, which had not been taken account of in conventional packing materials. In
particular, the packing material can easily concentrate a trace objective substance
contained in an extra dilute solution in an environment-related sample or a medical
sample and at the same time, can easily remove impurities or contaminants present
together. Accordingly, the packing material can facilitate various analyses with good
precision and is effective in the field over a wide range, for example, in the measurement
of harmful substances such as agricultural chemical in river water, the measurement
of residual agricultural chemicals in farm products and the measurement of drugs in
serum.
1. A packing material for solid phase extraction, comprising particles having an exclusion
limit molecular weight of from 1×103 to 1.5×104 in gel permeation chromatography using a standard polystyrene as the measuring sample.
2. The packing material for solid phase extraction as claimed in claim 1, wherein the
particle is a synthetic polymer particle obtained by polymerizing monomers containing
at least a crosslinkable monomer.
3. The packing material for solid phase extraction as claimed in claim 2, wherein the
synthetic polymer particle is a polymer of at least a crosslinkable monomer (A) and
a non-crosslinkable monomer (B).
4. The packing material for solid phase extraction as claimed in claim 3, which contains
an aromatic divinyl compound as the crosslinkable monomer (A) in an amount of 30%
by mass or more based on the total amount of monomers.
5. The packing material for solid phase extraction as claimed in claim 3 or 4, which
contains a polyhydric alcohol poly(meth)acrylic acid ester as the crosslinkable monomer
(A) in an amount of 10% by mass or more based on the total amount of monomers.
6. The packing material for solid phase extraction as claimed in any one of claims 3
to 5, which contains an N-vinylcarboxylic acid amide as the non-crosslinkable monomer
(B) in an amount of 5 to 60% by mass based on the total amount of monomers.
7. The packing material for solid phase extraction as claimed in claim 6, wherein the
N-vinylcarboxylic acid amide is N-vinylacetamide.
8. The packing material for solid phase extraction as claimed in any one of claims 1
to 7, which is packed into a column, a cartridge or a reservoir on use.
9. The packing material for solid phase extraction as claimed in any one of claims 1
to 8, which is used for concentrating an objective component and/or removing impurities
or contaminants.
10. The packing material for solid phase extraction as claimed in any one of claims 1
to 9, which has an average particle size of 1 to 200 µm.
11. A column for solid phase extraction, which is packed with the packing material for
solid phase extraction described in any one of claims 1 to 10.
12. A cartridge for solid phase extraction, which is packed with the packing material
for solid phase extraction described in any one of claims 1 to 10.
13. The column for solid phase extraction as claimed in claim 11, which is used for concentrating
an objective component and/or removing impurities or contaminants.
14. The cartridge for solid phase extraction as claimed in claim 12, which is used for
concentrating an objective component and/or removing impurities or contaminants.
15. A process for treating an environment- or medical sample, which uses the column for
solid phase extraction described in claim 11 or 13.
16. A process for treating an environment- or medical sample, which uses the cartridge
for solid phase extraction described in claim 12 or 14.
17. The process for treating an environment- or medical sample as claimed in claim 15
or 16, which is used for the treatment of a protein component-containing sample.
Amended claims in accordance with Rule 86(2) EPC.
1. A packing material for solid phase extraction, comprising particles having an exclusion
limit molecular weight of from 1×103 to 1.5×104 in gel permeation chromatography using a standard polystyrene as the measuring sample,
wherein the particle is a synthetic polymer particle obtained by polymerizing monomers
containing at least a crosslinkable monomer..
2. The packing material for solid phase extraction as claimed in claim 1, wherein the
synthetic polymer particle is a polymer of at least a crosslinkable monomer (A) and
a non-crosslinkable monomer (B).
3. The packing material for solid phase extraction as claimed in claim 2, which contains
an aromatic divinyl compound as the crosslinkable monomer (A) in an amount of 30%
by mass or more based on the total amount of monomers.
4. The packing material for solid phase extraction as claimed in claim 2 or 3, which
contains a polyhydric alcohol poly(meth)acrylic acid ester as the crosslinkable monomer
(A) in an amount of 10% by mass or more based on the total amount of monomers.
5. The packing material for solid phase extraction as claimed in any one of claims 2
to 4, which contains an N-vinylcarboxylic acid amide as the non-crosslinkable monomer
(B) in an amount of 5 to 60% by mass based on the total amount of monomers.
6. The packing material for solid phase extraction as claimed in claim 5, wherein the
N-vinylcarboxylic acid amide is N-vinylacetamide.
7. The packing material for solid phase extraction as claimed in any one of claims 1
to 6, which is packed into a column, a cartridge or a reservoir on use.
8. The packing material for solid phase extraction as claimed in any one of claims 1
to 7, which is used for concentrating an objective component and/or removing impurities
or contaminants.
9. The packing material for solid phase extraction as claimed in any one of claims 1
to 8, which has an average particle size of 1 to 200 µm.
10. A column for solid phase extraction, which is packed with the packing material for
solid phase extraction described in any one of claims 1 to 9.
11. A cartridge for solid phase extraction, which is packed with the packing material
for solid phase extraction described in any one of claims 1 to 9.
12. The column for solid phase extraction as claimed in claim 10, which is used for concentrating
an objective component and/or removing impurities or contaminants.
13. The cartridge for solid phase extraction as claimed in claim 11, which is used for
concentrating an objective component and/or removing impurities or contaminants.
14. A process for treating an environment- or medical sample, which uses the column for
solid phase extraction described in claim 10 or 12.
15. A process for treating an environment- or medical sample, which uses the cartridge
for solid phase extraction described in claim 11 or 13.
16. The process for treating an environment- or medical sample as claimed in claim 14
or 15, which is used for the treatment of a protein component-containing sample.